Energy efficient membrane-based process for co2 capture

ABSTRACT

Processes and systems for the energy efficient capture of CO 2  from a flue gas stream such as produced or resulting from power plant operation, are provided. The processes and systems integrate the use of high CO 2 /N 2  selectivity membranes and high CO 2  flux membranes, to capture CO 2 . Useful membranes can desirably be graphene oxide-based membranes.

CROSS REFERENCE TO RELATED APPLICATION

This application also claims the benefit of U.S. Provisional Patent Application Ser. No. 62/642,783, filed on 14 Mar. 2018. This co-pending Provisional Application is hereby incorporated by reference herein in its entirety and is made a part hereof, including but not limited to those portions which specifically appear hereinafter.

STATEMENT REGARDING FEDERALLY SPONSORED RESEARCH OR DEVELOPMENT

This invention was made with government support under grant DE-FE0031598 awarded by DOE NETL. The government has certain rights in the invention.

BACKGROUND OF THE INVENTION Field of the Invention

This invention relates generally to CO₂ capture and, more particularly, to such capture via or employing high selectivity membranes.

Description of Related Art

Amine absorption is the current DOE and industry benchmark technology for capture of CO₂ from power plant flue gases. DOE/NETL systems analysis studies estimated that using a chemical absorption with an aqueous monoethanolamine system to capture 90% of the CO₂ from flue gas will require an increase in the levelized cost of energy (LCOE) services of 75-85%. These values are well above the 2020 DOE NETL Sequestration Program post-combustion capture goal of 90% capture in existing plants with less than 35% increase in LCOE. Therefore, it is important to develop new advanced CO₂ capture technologies in order to maintain the cost-effectiveness of U.S. coal-fired power generation.

As identified above, amine absorption is the current DOE and industry benchmark technology for capture of CO₂ from power plant flue gases.

Additional technologies include:

1. Conventional Gas Separation Membrane Process:

Membrane Technology and Research (MTR) has developed a gas separation membrane, Polaris™, which exhibited pure-gas CO₂ permeance of about 1,650 GPU at 50° C. with an ideal selectivity (ratio of single gas permeances) of about 50 for CO₂/N₂. Ho et al. at Ohio State University (OSU) prepared zeolite/polymer composite membranes containing amine cover layer for CO₂ capture. The scaled membranes showed selectivities of 140 for binary CO₂/N₂ mixtures.

2. Hybrid Solvent/Membrane Process:

The University of Kentucky is developing an absorption solvent/membrane hybrid process. The absorption cycle uses aqueous ammonium and some typical alkyl amines. A T-type hydrophilic zeolite membrane is placed between the absorption and regeneration steps to reject water allowing a more concentrated solution to be sent to the regenerator. The high cost of zeolite membrane may limit the practical application of this technology; Caro et al. reported a cost of about US $3,000/m² for zeolite modules of which 10-15% is contributed to the membrane itself.

MTR and University of Texas at Austin are developing a hybrid piperazine solvent/Polaris™ membranes process for CO₂ capture. They reported that a hybrid series configuration requires a minimum of 70% removal by amine process, whereas a hybrid parallel configuration requires a minimum of 53% to 65% of the flue gas directed to the amine absorber.

3. Gas Technology Institute's Membrane Contactor Process:

Polyetheretherketone (PEEK) hollow fiber membrane contactor process is a hybrid membrane/absorption process in which flue gas is sent through the hollow fiber membrane tubes while a CO₂-selective solvent flows around the outer surface of the hollow fiber membrane tubes, allowing CO₂ to permeate through the membrane and absorb into the solvent. The CO₂-rich solvent is regenerated and sent back to the membrane absorber.

SUMMARY OF THE INVENTION

The invention relates to methods and systems for the separation and capture of CO₂ such as produced or resulting from power plant operation. In accordance with certain preferred embodiments, a transformational high CO₂/N₂ selectivity membrane [e.g., a graphene oxide (GO)-based membrane] can be installed in new or retrofitted into existing operations such as pulverized coal (PC) or natural gas power plants to separate and capture CO₂.

In one embodiment, the invention integrates a high CO₂/N₂ selectivity membrane [e.g. GO-based membranes] and a high CO₂ flux membrane. The invention offers new opportunities to explore significant reductions in the cost of CO₂ capture.

One aspect of the invention regards energy efficient processing for the capture of CO₂ such as produced upon operation of a power plant.

In accordance with one embodiment, such a process is particularly useful for the capture of CO₂ from a flue gas stream containing at least 5 vol. % CO₂. Such a process involves:

introducing the flue gas stream containing at least 5 vol. % CO₂ to a first stage membrane separator containing a first stage high CO₂/N₂ selectivity membrane to produce a first stage CO₂-depleted retentate stream and a first stage CO₂-enriched permeate stream;

introducing the first stage CO₂-depleted retentate stream to a second stage membrane separator containing a second stage high flux membrane to produce a second stage further CO₂-depleted retentate stream and a second stage CO₂-enriched permeate stream;

treating the second stage CO₂-enriched permeate stream to recover water and form a recyclable CO₂ stream;

introducing the recyclable CO₂ stream to the first stage membrane separator;

treating the first stage CO₂-enriched permeate stream to recover water and form a non-condensable CO₂-rich stream; and

compressing the CO₂ of the CO₂-rich stream to form a capture quantity of CO₂.

In accordance with one embodiment, such a process is particularly useful for the capture of CO₂ from a flue gas stream containing less than 5 vol. % CO₂. Such a process involves:

introducing the flue gas stream containing less than 5 vol. % CO₂ to a second stage membrane separator containing a second stage high flux membrane to produce a second stage CO₂-depleted retentate stream and a second stage CO₂-enriched permeate stream;

treating the second stage CO₂-enriched permeate stream to recover water and form a recyclable CO₂ stream;

introducing the recyclable CO₂ stream to a first stage membrane separator containing a first stage high CO₂/N₂ selectivity membrane to produce a first stage CO₂-depleted retentate stream and a first stage CO₂-enriched permeate stream;

treating the first stage CO₂-enriched permeate stream to recover water and form a non-condensable CO₂-rich stream;

introducing the first stage CO₂-depleted retentate stream to the second stage membrane separator; and

compressing the CO₂-rich stream to a sequestration pressure.

Another aspect of the invention regards s system for capture of CO₂ from a flue gas stream.

In accordance with one embodiment, such a system includes a first stage membrane separator containing a first stage high CO₂/N₂ selectivity membrane. A first stage vacuum pump is included to provide a vacuum on a permeate side of the first stage high CO₂/N₂ selectivity membrane. The first stage membrane separator produces a first stage CO₂-depleted retentate stream and a first stage CO₂-enriched permeate stream. The system further includes a second stage membrane separator containing a second stage high flux membrane, with the second stage separator receiving the CO₂-depleted retentate stream. A second stage vacuum pump is included to provide a vacuum on a permeate side of the second stage high flux membrane. The second stage membrane separator produces a second stage CO₂-depleted retentate stream and a second stage CO₂-enriched permeate stream.

As used herein, gas permeance of membranes is customarily expressed in GPU (Gas Permeation Unit, 1 GPU=1×10⁻⁶ cm³ (STP)/cm²·s·cmHg=3.348×10⁻¹⁰ mol/(m²·s·Pa)), and is calculated by the equation:

$\left( {P_{i}\text{/}l} \right) = \frac{J_{i}}{\Delta \; P_{i}A}$

where:

(P_(i)/l) denotes the gas permeance of “i”;

J_(i) denotes the gas molar flow rate through the membrane (mol/s);

ΔP_(i) denotes the gas partial pressure difference between feed and permeate sides (Pa); and

A denotes the membrane active area (m²).

As used herein, gas selectivity (a_(ij)) of membranes can be calculated by the equation:

a _(ij)=(P _(i) /l)/(P _(j) /l)

BRIEF DESCRIPTION OF THE DRAWINGS

Objects and features of this invention will be better understood from the following description taken in conjunction with the drawings, wherein:

FIG. 1 is a simplified process flow diagram illustrating application of processing in accordance with one embodiment of the invention.

FIG. 2 is a simplified process flow diagram illustrating application of processing in accordance with an alternative embodiment of the invention.

DETAILED DESCRIPTION

FIG. 1 is a process flow diagram of a processing system, generally designated by the reference numeral 110, illustrating application of processing in accordance with one embodiment of the invention. As detailed below and in accordance with one embodiment of the invention, the processing system 110 can advantageously energy efficiently process the capture of CO₂ from a flue gas stream containing at least 5 vol. % CO₂. For example, such embodiment might find particular application in the processing of CO₂-containing flue gas streams produced or resulting from power plant operations utilizing pulverized coal (PC), including installed in new or retrofitted into existing operations. It is to be understood, however, that the broader practice of the invention is not necessarily so limited.

In the processing system 110, a blower 112 is used to send a flue gas (stream 114 and such as containing at least 5 vol. % CO₂) to a first stage membrane separator 116 such as including or containing a first stage high CO₂/N₂ selectivity membrane 120 [e.g., a high selectivity membrane (such as, a graphene oxide (GO)-based membrane) having or exhibiting a CO₂/N₂ selectivity >120, for example)]. The stream 114 can desirably be composed of flue gas such as produced or resulting from operation of a power plant, shown as stream 122, and a recycle stream 124, described further below. A vacuum pump 126 is used on a permeate side of the membrane 120 to provide a vacuum [e.g., a vacuum of ˜0.2 bar] such as to create a driving force for separation. A CO₂-depleted retentate or residue stream 128, such as containing less than 5 vol. % CO₂, leaves the first stage membrane separator 116 and is sent to a second stage membrane separator 130 such as including or containing a second stage high flux membrane 132 [e.g., a high permeance membrane (such as having or exhibiting a CO₂ permeance >1000 GPU, for example)]. A vacuum pump 136 is used on a permeate side of the membrane 132 to provide a vacuum [e.g., a vacuum of ˜0.2 bar] such as to create a driving force for separation. Treated flue gas (e.g., the stream 136) can be further processed or disposed such as may be desired such as by being sent to the stack, for example.

The CO₂-enriched permeate from the first stage membrane separator 116 (e.g., the stream 140) can advantageously be processed to remove most of the water as liquid (e.g., shown as a stream 142). As shown, such water removal processing may involve cooling, such as via a gas cooler 144 and subsequent separation such as via a water knockout unit 146. A resulting stream 150 of non-condensables and such as containing or including greater than 95 vol. % CO₂ can be forwarded, such as a stream 152 and can be advantageously processed. e.g., compressed in stages at high pressures form a stream of CO₂ for sequestration.

The permeate stream 160 from the second stage membrane separator 130 can be similarly processed to remove most of the water as liquid (e.g., shown as a stream 162) and is then recycled (see stream 124) to the feed to a first stage membrane separator 116. As shown, such water removal processing may involve cooling, such as via a gas cooler 164 and subsequent separation such as via a water knockout unit 166.

In the processing system 110, the membrane 120 of the first stage membrane separator 116 is a high selectivity membrane (target CO₂/N₂ selectivity ≥200), whereas the membrane 132 of the second stage membrane separator 130 is a high-flux membrane (target CO₂ permeance ≥2,500 GPU).

While the processing system 110, described above, is believed to have particular applicability to the processing or capture of CO₂ from a flue gas stream containing at least 5 vol. % CO₂, such as produced or resulting from power plant operations utilizing pulverized coal, with appropriate modification, such or a similar system can be applied to the processing or capture of CO₂ from a flue gas stream containing less than 5 vol. % CO₂, such as produced or resulting from power plant operations utilizing natural gas, for example.

For CO₂ capture from natural gas-fired power plants, such as produce, form or result in flue gas containing less than 5 vol. % CO₂, a system or processing arrangement such as shown in FIG. 1, can be modified such that the low-CO₂-concentration flue gas (e.g., ˜4-5% CO₂) will be directly fed to the second stage membrane separator and with high purity CO₂ (≥95%) will still be collected from the permeate side of the membrane of the first stage membrane separator. Such a system and processing will be described below making reference to FIG. 2.

FIG. 2 is a process flow diagram of a processing system, generally designated by the reference numeral 210, illustrating application of processing in accordance with one embodiment of the invention. As detailed below and in accordance with one embodiment of the invention, the processing system 210 can advantageously energy efficiently process the capture of CO₂ from a flue gas stream containing less than 5 vol. % CO₂. For example, such embodiment might find particular application in the processing of CO₂-containing flue gas streams produced or resulting from power plant operations utilizing natural gas, including installed in new or retrofitted into existing operations. It is to be understood, however, that the broader practice of the invention is not necessarily so limited.

In the processing system 210, a blower 212 is used to boost the pressure of the flue gas (stream 213), such as from 14.2 psia to 21.2 psia (e.g., Δ7 psig), prior to sending the elevated pressure flue gas stream 214 and such as containing less than 5 vol. % CO₂ to a second stage membrane separator 216 such as including or containing a second stage high flux membrane 220 [e.g., a high permeance membrane (such as having or exhibiting a CO₂ permeance >1000 GPU, for example)].

A vacuum pump 222 is used on a permeate side of the membrane 220 to provide a vacuum [e.g., a vacuum of ˜0.2 bar (2.9 psia)] such as to create a driving force for separation. A CO₂-depleted retentate stream 226 can be further processed or disposed such as may be desired such as by being sent to the stack, for example.

The permeate stream 230 leaving the second stage membrane separator 216 can advantageously be processed to remove most of the water as liquid (e.g., shown as a stream 232). As shown, such water removal processing may involve cooling, such as via a gas cooler 234 and subsequent separation such as via a water knockout unit 236. A resulting stream 240 of non-condensables is sent (such as via a blower 242) as feed to first stage membrane separator 246 such as including or containing a first stage high CO₂/N₂ selectivity membrane 250 [e.g., a high selectivity membrane (such as a graphene oxide (GO)-based membrane) having or exhibiting a CO₂/N₂ selectivity >120, for example)]. A vacuum pump 252 is used on a permeate side of the membrane 250 to provide a vacuum [e.g., a vacuum of ˜0.2 bar] such as to create a driving force for separation. A CO₂-depleted retentate or residue stream 254 leaves the first stage membrane separator 246 and is fed or introduced to the second stage membrane separator 216 such as including or containing the second stage high flux membrane 220 [e.g., a high permeance membrane (such as having or exhibiting a CO₂ permeance >1000 GPU, for example)]. The permeate stream 260 from the first stage membrane separator 246 can advantageously be processed to remove most of the water as liquid (e.g., shown as a stream 262). As shown, such water removal processing may involve cooling, such as via a gas cooler 264 and subsequent separation such as via a water knockout unit 266. A resulting stream 270 of non-condensables and such as containing or including greater than 95 vol. % CO₂ can be forwarded, such as a stream 272 and can be advantageously processed. e.g., compressed in stages at high pressures form a stream of CO₂ for sequestration.

While the broader practice of the invention does not necessarily require that suitable high selectivity membranes in or for the first stage membrane separator and suitable high-flux membranes in or for the second stage membrane separator be of a specific or particular form or construction, it has been found that graphene oxide (GO)-based membranes can be usefully employed for such high selectivity membranes and/or such high-flux membranes. U.S. Pat. No. 9,795,931 to Yu et al., issued 24 Oct. 2017, is an example of a patent describing some such type of graphene oxide (GO)-based membranes.

The target CO₂ permeance and CO₂/N₂ separation performances for high selectivity membranes (Membrane I) and high-flux membranes (Membrane II) in accordance with certain preferred aspects of the invention are listed or shown below in Table 1.

TABLE 1 Target CO₂/N₂ separation performance for Membranes I and II. CO₂ permeance Membrane (GPU) CO₂/N₂ selectivity Membrane I (high selectivity) 1,000 200 Membrane II (high-flux) 2,500 20

Is respectively noted that 70% CO₂ removal can be achieved by a single Membrane I stage. For 90% CO₂ removal, a two-stage membrane process may be desired.

An economic evaluation for parasitic energy requirements and capital costs was based on analysis and methods as presented in the 2013 version of the DOE Baseline Report, i.e., DOE/NETL-2010/1397, Volume 1: Bituminous Coal and Natural Gas to Electricity, Cost and Performance Baseline for Fossil Energy Plants, Revision 2a, p 63, September, 2013. Costs for fuel and consumables (in 2012 $) except membrane cost, were specified by the DOE. A target membrane cost of $30/m² (in 2012 $) was used for this economic evaluation. For a 550 MW_(e) (net) power plant, the required membrane area is 2.5×10⁶ m². Table 2 shows the constituents that make up the COE, and total COE. As shown, the process can achieve 90% CO₂ capture rate with 95% CO₂ purity at a COE 26.4% less than the baseline approach (DOE case B12B). For a 70% CO₂ capture case, the COE is 30.4% lower than the baseline approach.

TABLE 2 Constituents of COE, and total COE for carbon capture. CO₂ capture rate 90% using 90% integrated 70% using DOE Case Membranes I Membrane I Constituents of COE ($/MWh) B12B and II only Total capital costs 72.2 51.2 47.2 Total fixed operating costs 15.4 6.9 6.4 Total variable operating costs 14.7 9.0 8.3 Coal 30.9 30.9 30.9 Total COE excluding TS&M 133.2 98.0 92.8 ($/MWh) % of COE less than DOE Case — 26.4 30.4 B12B

The current invention, functionally, has the benefits of a hybrid system but the simplicity of a membrane system which also reduces the up-front installation costs and footprint and does not add circulating liquids to the power plant environment. Therefore, it facilitates the ease of integration into a power plant.

The current invention serves as a platform for CO₂ capture from both coal-fired and natural gas-fired power plants. This invention will provide step reductions in CO₂ capture cost and energy penalties and will meet DOE's performance and cost goals. This invention is well suited for new and existing pulverized coal power plants due to the reduced footprint requirement and a much lower visual impact.

While in the foregoing detailed description this invention has been described in relation to certain preferred embodiments thereof, and many details have been set forth for purposes of illustration, it will be apparent to those skilled in the art that the invention is susceptible to additional embodiments and that certain of the details described herein can be varied considerably without departing from the basic principles of the invention.

Moreover, those skilled in the art and guided by the teachings herein identified, described or discussed will understand and appreciate that the subject development encompasses a variety of features and is thus capable of manifestation in a variety of specific forms or embodiments and is thus not to be construed as limited to the specific forms or embodiments herein identified or described. 

What is claimed includes:
 1. An energy efficient process for the capture of CO₂ from a flue gas stream containing at least 5 vol. % CO₂, the process comprising: introducing the flue gas stream containing at least 5 vol. % CO₂ to a first stage membrane separator containing a first stage high CO₂/N₂ selectivity membrane to produce a first stage CO₂-depleted retentate stream and a first stage CO₂-enriched permeate stream; introducing the first stage CO₂-depleted retentate stream to a second stage membrane separator containing a second stage high flux membrane to produce a second stage further CO₂-depleted retentate stream and a second stage CO₂-enriched permeate stream; treating the second stage CO₂-enriched permeate stream to recover water and form a recyclable CO₂ stream; introducing the recyclable CO₂ stream to the first stage membrane separator; treating the first stage CO₂-enriched permeate stream to recover water and form a non-condensable CO₂-rich stream; and compressing the CO₂ of the CO₂-rich stream to form a capture quantity of CO₂.
 2. The process of claim 1 wherein the first stage high CO₂/N₂ selectivity membrane is a graphene oxide-based membrane.
 3. The process of claim 1 wherein the first stage high CO₂/N₂ selectivity membrane has a target CO₂/N₂ selectivity of ≥120.
 4. The process of claim 1 wherein second stage high flux membrane is a graphene oxide-based membrane.
 5. The process of claim 1 wherein second stage high flux membrane has a target CO₂ permeance of ≥1,000 GPU.
 6. In a power plant operation that produces a flue gas stream containing at least 5 vol. % CO₂, the process of claim 1 for capture of CO₂ from the flue gas stream.
 7. An energy efficient process for the capture of CO₂ from a flue gas stream containing less than 5 vol. % CO₂, the process comprising: introducing the flue gas stream containing less than 5 vol. % CO₂ to a second stage membrane separator containing a second stage high flux membrane to produce a second stage CO₂-depleted retentate stream and a second stage CO₂-enriched permeate stream; treating the second stage CO₂-enriched permeate stream to recover water and form a recyclable CO₂ stream; introducing the recyclable CO₂ stream to a first stage membrane separator containing a first stage high CO₂/N₂ selectivity membrane to produce a first stage CO₂-depleted retentate stream and a first stage CO₂-enriched permeate stream; treating the first stage CO₂-enriched permeate stream to recover water and form a non-condensable CO₂-rich stream; introducing the first stage CO₂-depleted retentate stream to the second stage membrane separator; and compressing the CO₂-rich stream to a sequestration pressure.
 8. The process off claim 7 wherein the first stage high CO₂/N₂ selectivity membrane is a graphene oxide-based membrane.
 9. The process of claim 7 wherein the first stage high CO₂/N₂ selectivity membrane has a target CO₂/N₂ selectivity of ≥120.
 10. The process of claim 7 wherein second stage high flux membrane is a graphene oxide-based membrane.
 11. The process of claim 7 wherein second stage high flux membrane has a target CO₂ permeance of ≥1,000 GPU.
 12. In a power plant operation that produces a flue gas stream containing less than 5 vol. % CO₂, the process of claim 7 for capture of CO₂ from the flue gas stream.
 13. A system for capture of CO₂ from a flue gas stream, the system comprising: a first stage membrane separator containing a first stage high CO₂/N₂ selectivity membrane; a first stage vacuum pump to provide a vacuum on a permeate side of the first stage high CO₂/N₂ selectivity membrane; wherein the first stage membrane separator produces a first stage CO₂-depleted retentate stream and a first stage CO₂-enriched permeate stream; a second stage membrane separator containing a second stage high flux membrane, the second stage separator receiving the CO₂-depleted retentate stream; a second stage vacuum pump to provide a vacuum on a permeate side of the second stage high flux membrane; wherein the second stage membrane separator produces a second stage CO₂-depleted retentate stream and a second stage CO₂-enriched permeate stream.
 14. The system of claim 13 wherein the flue gas stream contains at least 5 vol. % CO₂, the system further includes a feed line to introduce the flue gas stream containing at least 5 vol. % CO₂ to the first stage membrane separator.
 15. The system of claim 13 wherein the flue gas stream contains less than 5 vol. % CO₂, the system further includes a feed line to introduce the flue gas stream containing less than 5 vol. % CO₂ to the second stage membrane separator.
 16. The system of claim 13 additionally comprising a cooler to cool at least one of the first stage CO₂-enriched permeate stream and the second stage CO₂-enriched permeate stream to condense and separate water therefrom.
 17. The system of claim 13 wherein the first stage high CO₂/N₂ selectivity membrane is a graphene oxide-based membrane.
 18. The system of claim 13 wherein the first stage high CO₂/N₂ selectivity membrane has a target CO₂/N₂ selectivity of ≥120.
 19. The process of claim 13 wherein second stage high flux membrane is a graphene oxide-based membrane.
 20. The process of claim 13 wherein second stage high flux membrane has a target CO₂ permeance of ≥1,000 GPU. 